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JPH08257404A - Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide - Google Patents

Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide

Info

Publication number
JPH08257404A
JPH08257404A JP7063809A JP6380995A JPH08257404A JP H08257404 A JPH08257404 A JP H08257404A JP 7063809 A JP7063809 A JP 7063809A JP 6380995 A JP6380995 A JP 6380995A JP H08257404 A JPH08257404 A JP H08257404A
Authority
JP
Japan
Prior art keywords
weight
parts
nitrogen oxides
catalyst material
carrier
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP7063809A
Other languages
Japanese (ja)
Inventor
Masaharu Nonoguchi
正治 野々口
Hitoshi Matsunosako
等 松之迫
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kyocera Corp
Original Assignee
Kyocera Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kyocera Corp filed Critical Kyocera Corp
Priority to JP7063809A priority Critical patent/JPH08257404A/en
Publication of JPH08257404A publication Critical patent/JPH08257404A/en
Pending legal-status Critical Current

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  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

(57)【要約】 【目的】水蒸気存在下や、高酸素濃度雰囲気下、W/F
値が高くとも、低温域まで広範囲に高いNOX 還元分解
作用を有し、省エネルギー、省資源及び地球温暖化防止
用の各種内燃機関の排気ガスや、NOX 含有有害物質の
浄化。 【構成】窒素酸化物除去用酸化物触媒材料として、Ni
とGaを主金属元素として含有する主結晶相がスピネル
型構造の複合酸化物とアルミナから成る担持体にPt又
はPdを担持して窒素酸化物除去用酸化物触媒材料とな
し、該酸化物触媒材料を高濃度の酸素が存在し、かつ炭
化水素等の還元性ガスが存在する酸化雰囲気中で、窒素
酸化物を含む排気ガスと接触させて窒素酸化物を還元分
解し除去する。
(57) [Summary] [Purpose] W / F in the presence of water vapor or high oxygen concentration atmosphere
Even if the value is high, it has a high NO x reduction decomposition effect in a wide range even in low temperature range, and purifies exhaust gas of various internal combustion engines for energy saving, resource saving and prevention of global warming and harmful substances containing NO x . [Structure] Ni as an oxide catalyst material for removing nitrogen oxides
A Pt or Pd is supported on a carrier whose main crystal phase containing Al and Ga as main metal elements is a spinel-type composite oxide and alumina to form an oxide catalyst material for removing nitrogen oxides. The material is brought into contact with an exhaust gas containing nitrogen oxides in an oxidizing atmosphere in which a high concentration of oxygen is present and a reducing gas such as a hydrocarbon is present to reduce and decompose the nitrogen oxides.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、窒素酸化物を還元除去
することのできる新規な酸化物触媒材料並びにこれを用
いて排気ガス中の窒素酸化物を除去する方法に関するも
ので、とりわけ排気ガス温度が低いディーゼルエンジン
等の窒素酸化物還元除去用触媒並びに該触媒を用いて低
温で排気ガス中の窒素酸化物を除去する方法に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a novel oxide catalyst material capable of reducing and removing nitrogen oxides, and a method for removing nitrogen oxides in exhaust gas using the same, and more particularly to exhaust gas. The present invention relates to a catalyst for nitrogen oxide reduction and removal in diesel engines and the like having a low temperature, and a method for removing nitrogen oxide in exhaust gas at low temperature using the catalyst.

【0002】[0002]

【従来の技術】近年、各種汚染物質による大気の汚れが
大きな社会問題となり、その中でも大気汚染の移動発生
源となっている自動車の排気ガス中のNOX 、COX
の有害物質を分解、除去する方法の開発が急務となって
いる。
2. Description of the Related Art In recent years, air pollution caused by various pollutants has become a major social problem, and among them, harmful substances such as NO x and CO x in exhaust gas of automobiles, which are sources of migration of air pollution, are decomposed. There is an urgent need to develop a method for removal.

【0003】従来より自動車の排気ガス中のNOX 、C
X 等の有害物質を分解、除去する方法として、一酸化
炭素(CO)及び炭化水素(CX X )の酸化と、窒素
酸化物(NOX )の還元を同時に行う三元触媒を用いる
方法が採用されてきた。
Conventionally, NO x , C in the exhaust gas of automobiles
Decomposing harmful substances O X such as a method of removing, using an oxidation of carbon monoxide (CO) and hydrocarbons (C X H X), nitrogen oxide three-way catalyst to perform reduction at the same time the (NO X) The method has been adopted.

【0004】そのような方法に用いられる三元触媒とし
ては、γ−アルミナ(Al2 3 )で被覆したコージェ
ライト等の耐火物に、パラジウム(Pd)、白金(P
t)、ロジウム(Rh)等の貴金属を担持したものが用
いられていた。
As a three-way catalyst used in such a method, a refractory material such as cordierite coated with γ-alumina (Al 2 O 3 ) is used, and palladium (Pd) or platinum (Pd) is used.
t) and those carrying a noble metal such as rhodium (Rh) have been used.

【0005】しかしながら、前記三元触媒は、およそ
0.5%程度の低酸素濃度においてのみ排気ガスの浄化
を効率よく行うことができるが、排気ガスの酸素濃度が
1%を越えるような高濃度域では有効に働かなくなると
いう欠点がある。
However, although the three-way catalyst can efficiently purify the exhaust gas only at a low oxygen concentration of about 0.5%, the three-way catalyst has a high oxygen concentration of more than 1%. It has the drawback of not working effectively in the region.

【0006】そこで、通常は排気ガス中の酸素濃度を測
定し、CO及びCX X 、NOX を高い浄化率で処理し
得る理論等量値に近い範囲の空燃比となるように制御す
ることが行われているが、前記CO及びCX X と、N
X の発生メカニズムが相反する特性を有するため、限
られた状態での燃焼を維持しなければならず、それより
高い酸素濃度中での排気ガス浄化はほとんどできていな
いのが現状である。
Therefore, normally, the oxygen concentration in the exhaust gas is measured, and the air-fuel ratio is controlled so that CO, C X H X , and NO X can be processed at a high purification rate, and the air-fuel ratio is in a range close to the theoretical equivalent value. However, the CO and C X H X , and N
Since O X generation mechanisms have contradictory properties, it is necessary to support combustion in a state where limited exhaust gas purification at a high oxygen concentration in than it is at present, not hardly.

【0007】更に、昨今、省エネルギー、省資源も叫ば
れていることから、ガソリンエンジンにおいては、低燃
費化を図るために希薄燃焼方式の研究開発が行われてい
るが、この場合、排気ガス中の酸素濃度は数%と高くな
り、触媒の貴金属が酸素被毒により排気ガスの浄化がで
きなくなるという欠点がある。
Further, since energy saving and resource saving have recently been demanded, in a gasoline engine, research and development of a lean combustion system have been carried out in order to achieve low fuel consumption. Has a disadvantage that the noble metal of the catalyst cannot be purified by exhaust gas due to oxygen poisoning.

【0008】またディーゼルエンジンにおいても、現在
の燃焼方式では排気ガス中の酸素濃度が高いために排気
ガスの浄化が全くなされていないのが現状である。
Also in the diesel engine, in the present combustion system, the exhaust gas is not purified at all because the oxygen concentration in the exhaust gas is high.

【0009】一方、約1000℃以上の高温で発生し、
燃焼温度が高くなるほどその濃度が高くなるNOX を効
果的に浄化する方法としては、前記以外にアンモニアを
用いた選択的接触還元法があるが、工場等の固定式の燃
焼装置における酸素濃度の高い排気ガス中のNOX の浄
化に対しては有効ではあるものの、本方法を自動車等の
移動式燃焼装置に適用することは安全性の面で問題があ
る。
On the other hand, it occurs at a high temperature of about 1000 ° C. or higher,
As a method of effectively purifying NO X , the concentration of which increases as the combustion temperature increases, there is a selective catalytic reduction method using ammonia in addition to the above method. Although effective for purifying NO x in high exhaust gas, applying this method to a mobile combustion device such as an automobile has a problem in safety.

【0010】そこで、前記諸問題を解消するものとし
て、金属を担持した疎水性ゼオライトを触媒として炭化
水素と接触させながらNOX を除去する方法が、特開平
4−349938号公報等に提案されている。
[0010] Therefore, as to solve the above problems, a method of the hydrophobic zeolite carrying the metal removing NO X while in contact with the hydrocarbon as a catalyst, is proposed in JP-A 4-349938 Patent Publication There is.

【0011】[0011]

【発明が解決しようとする課題】しかしながら、前記金
属を担持した疎水性ゼオライトを触媒とするものは耐水
性が悪く、例えば、ディーゼルエンジンのように排気ガ
ス中に水分を含む場合には、水蒸気の存在によりNOX
の浄化率の経時低下が大きいという課題があり、更に、
耐熱性においても前記触媒は構造破壊等の問題があり、
耐熱性、耐水性に優れ、かつ350℃以下の低温度域ま
での広範囲に及ぶNO還元活性を示す触媒材料が望まれ
ていた。
However, a catalyst using the above-mentioned metal-supporting hydrophobic zeolite as a catalyst has poor water resistance. For example, when water is contained in exhaust gas such as a diesel engine, water vapor NO X by existence
There is a problem that the purification rate of
Even in heat resistance, the catalyst has problems such as structural destruction,
A catalyst material having excellent heat resistance and water resistance and having NO reduction activity over a wide range up to a low temperature region of 350 ° C. or less has been desired.

【0012】[0012]

【発明の目的】本発明はアンモニア等の毒性の強い還元
剤を必要とせず、ディーゼルエンジン等の水分を含む酸
素濃度の高い比較的低温の排気ガスを、該排気ガスの流
速が高速度であっても、有効に排気ガス中のNOX を浄
化することができる耐熱性に優れたNO還元活性温度域
が広い触媒材料並びにそれを用いた窒素酸化物除去方法
を提供するものである。
SUMMARY OF THE INVENTION The present invention does not require a highly toxic reducing agent such as ammonia, and allows a relatively low temperature exhaust gas having a high oxygen concentration containing water such as a diesel engine to have a high flow velocity. Even so, it is intended to provide a catalyst material which is capable of effectively purifying NO X in exhaust gas and which has excellent heat resistance and has a wide NO reduction activation temperature range, and a nitrogen oxide removing method using the same.

【0013】[0013]

【課題を解決するための手段】本発明は、上記課題に鑑
みなされたもので、ニッケル(Ni)およびガリウム
(Ga)を主たる金属元素として含有する結晶相がスピ
ネル型構造である複合酸化物にアルミナ(Al2 3
を混合した担持体に、貴金属である白金(Pt)を担持
した酸化物触媒材料が、水蒸気存在下の高い酸素濃度で
も300℃以下の低温度域に最大の触媒活性を持つ優れ
た低温活性を示し、また前記担持体にパラジウム(P
d)を担持した酸化物触媒材料が、水蒸気存在下の高い
酸素濃度でも300℃から500℃の広い温度範囲に及
ぶ優れた触媒活性を長期にわたり有することを見出した
ものである。
The present invention has been made in view of the above problems, and provides a composite oxide having a spinel structure as a crystal phase containing nickel (Ni) and gallium (Ga) as main metal elements. Alumina (Al 2 O 3 )
An oxide catalyst material in which platinum (Pt), which is a noble metal, is supported on a carrier in which is mixed, has an excellent low-temperature activity with a maximum catalytic activity in a low temperature range of 300 ° C or lower even in a high oxygen concentration in the presence of water vapor. In addition, palladium (P
It has been discovered that the oxide catalyst material supporting d) has excellent catalytic activity over a wide temperature range of 300 ° C. to 500 ° C. for a long time even at a high oxygen concentration in the presence of water vapor.

【0014】即ち、本発明の窒素酸化物除去用酸化物触
媒材料は、ニッケル(Ni)およびガリウム(Ga)を
主たる金属元素として含有し、その結晶相がスピネル型
構造を有する複合酸化物粉末とAl2 3 粉末を混合し
た担持体に、白金(Pt)またはパラジウム(Pd)を
前記担持体100重量部に対して0.01〜1.0重量
部担持したことを特徴とするものである。
That is, the oxide catalyst material for removing nitrogen oxides of the present invention contains a composite oxide powder containing nickel (Ni) and gallium (Ga) as main metal elements and having a crystal phase having a spinel type structure. 0.01 to 1.0 part by weight of platinum (Pt) or palladium (Pd) is carried on a carrier mixed with Al 2 O 3 powder based on 100 parts by weight of the carrier. .

【0015】特に、前記白金(Pt)を前記担持体10
0重量部に対して0.03〜1.0重量部、または前記
パラジウム(Pd)を前記担持体100重量部に対して
0.01〜0.7重量部担持した酸化物触媒材料である
ことがより好ましく、とりわけ前記白金(Pt)を0.
03〜0.7重量部、または前記パラジウム(Pd)を
0.01〜0.5重量部担持したものが最も好ましい。
In particular, the platinum (Pt) is added to the carrier 10.
0.03 to 1.0 part by weight with respect to 0 part by weight, or 0.01 to 0.7 part by weight of the palladium (Pd) with respect to 100 parts by weight of the support, and an oxide catalyst material. Is more preferable, and in particular, the platinum (Pt) is less than 0.
It is most preferable to carry 03 to 0.7 parts by weight, or 0.01 to 0.5 parts by weight of the palladium (Pd).

【0016】更に、本発明の窒素酸化物除去方法は、高
濃度の酸素と還元性を有する炭素含有ガスが存在する酸
化雰囲気中で、ニッケル(Ni)とガリウム(Ga)を
主たる金属元素として含有する結晶相がスピネル型構造
である複合酸化物に、Al23 を混合した担持体に、
白金(Pt)またはパラジウム(Pd)を前記担持体1
00重量部に対して0.01〜1.0重量部担持して成
る酸化物触媒材料と、窒素酸化物を含む排気ガスを接触
させることを特徴とするものである。
Further, the method for removing nitrogen oxides of the present invention contains nickel (Ni) and gallium (Ga) as main metal elements in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. To a carrier prepared by mixing Al 2 O 3 with a complex oxide whose crystal phase is a spinel structure,
The carrier 1 containing platinum (Pt) or palladium (Pd)
It is characterized in that the exhaust gas containing nitrogen oxides is brought into contact with the oxide catalyst material which is supported by 0.01 to 1.0 parts by weight with respect to 00 parts by weight.

【0017】なかでも、前記酸化物触媒材料として、前
記白金(Pt)を前記担持体100重量部に対して0.
03〜1.0重量部、または前記パラジウム(Pd)を
前記担持体100重量部に対して0.01〜0.7重量
部担持したものを用いることがより望ましく、更に、前
記白金(Pt)を0.03〜0.7重量部、または前記
パラジウム(Pd)を0.01〜0.5重量部担持した
ものを用いることが最も好ましい。
Above all, the platinum (Pt) as the oxide catalyst material is 0.1% based on 100 parts by weight of the carrier.
It is more desirable to use 03 to 1.0 parts by weight, or 0.01 to 0.7 parts by weight of the palladium (Pd) supported on 100 parts by weight of the support, and further the platinum (Pt). It is most preferable to use 0.03 to 0.7 part by weight of Pd, or 0.01 to 0.5 part by weight of the palladium (Pd).

【0018】本発明において、前記窒素酸化物除去用酸
化物触媒材料として、前記担持体に貴金属である白金
(Pt)またはパラジウム(Pd)を担持体100重量
部に対して0.01重量部未満しか担持しなかった場合
には、350℃以下の低温域ではNO還元活性が現れ
ず、逆に、1.0重量部を越えると、還元剤の単純酸化
反応だけが進行し、NO還元反応が現れない。
In the present invention, as the oxide catalyst material for removing nitrogen oxides, platinum (Pt) or palladium (Pd), which is a noble metal, is added to the support in an amount of less than 0.01 part by weight based on 100 parts by weight of the support. In the case of only supporting it, NO reduction activity does not appear in the low temperature region of 350 ° C. or lower, and conversely, when it exceeds 1.0 part by weight, only the simple oxidation reaction of the reducing agent proceeds, and the NO reduction reaction occurs. It does not appear.

【0019】従って、前記窒素酸化物除去用酸化物触媒
材料は、前記担持体に白金(Pt)またはパラジウム
(Pd)を、担持体100重量部に対して0.01〜
1.0重量部担持して成るものに限定され、触媒活性の
点からは白金(Pt)を前記担持体100重量部に対し
て0.03〜1.0重量部、または前記パラジウム(P
d)を前記担持体100重量部に対して0.01〜0.
7重量部担持したものがより望ましく、とりわけ広範囲
の温度域での触媒活性という点からは前記白金(Pt)
を前記担持体100重量部に対して0.03〜0.7重
量部、または前記パラジウム(Pd)を前記担持体10
0重量部に対して0.01〜0.5重量部担持したもの
が最も好ましい。
Therefore, in the oxide catalyst material for removing nitrogen oxides, platinum (Pt) or palladium (Pd) is added to the support in an amount of 0.01 to 100 parts by weight.
The amount of platinum (Pt) is limited to 1.0 part by weight, and from the viewpoint of catalytic activity, platinum (Pt) is 0.03 to 1.0 part by weight, or palladium (P) is added to 100 parts by weight of the support.
0.01 to 0.d) based on 100 parts by weight of the carrier.
It is more desirable to support 7 parts by weight, and especially from the viewpoint of catalytic activity in a wide temperature range, the platinum (Pt)
0.03 to 0.7 parts by weight with respect to 100 parts by weight of the carrier, or the palladium (Pd) added to the carrier 10.
It is most preferable to support 0.01 to 0.5 parts by weight with respect to 0 parts by weight.

【0020】尚、前記複合酸化物はニッケル(Ni)と
ガリウム(Ga)を主たる金属元素として含有し、一般
式としてNiGa2 4 で表されるスピネル型構造の結
晶相を有するものであり、該複合酸化物のNiとGaの
相関は、Niに対するGaの蛍光X線分析によるカウン
ト比で論ずると、触媒活性の点からは1.4以上が望ま
しく、とりわけ1.5以上が最も好ましい。
The composite oxide contains nickel (Ni) and gallium (Ga) as main metal elements and has a spinel type crystal phase represented by NiGa 2 O 4 as a general formula. The correlation between Ni and Ga of the composite oxide is preferably 1.4 or more, and most preferably 1.5 or more, from the viewpoint of catalytic activity, in terms of the count ratio of Ga to Ni by fluorescent X-ray analysis.

【0021】また、前記Al2 3 は高い比表面積を有
するものが適当であると考えられ、実用的には60m2
/g以上が望ましく、また、Al2 3 混合量による触
媒活性の変化は少ないものの、その混合量は20〜70
重量%が好ましく、25〜60重量%が最も望ましい。
Further, it is considered appropriate that the Al 2 O 3 has a high specific surface area, and 60 m 2 is practically used.
/ G or more is desirable, and although the change in catalyst activity due to the Al 2 O 3 mixed amount is small, the mixed amount is 20 to 70.
Weight percent is preferred and 25-60 weight percent is most desirable.

【0022】更に、前記複合酸化物にAl2 3 を混合
した担持体に、貴金属である白金(Pt)またはパラジ
ウム(Pd)を前記担持体100重量部に対して合計
0.01〜1.0重量部担持した酸化物触媒材料と、窒
素酸化物を含む排気ガスを接触させる際、該排気ガス雰
囲気中に、還元剤としてC2 4 、C3 6 、C3 8
等の炭化水素、CH3 OH、C2 5 OH等のアルコー
ルや、CO等の還元性を有する炭素ガス等を含有させ
て、前記触媒材料と接触させると、NOX 還元性が一層
高くなる。
Further, platinum (Pt) or palladium (Pd), which is a noble metal, is added to a carrier obtained by mixing the composite oxide with Al 2 O 3 in a total amount of 0.01 to 1. When the oxide catalyst material supporting 0 parts by weight and the exhaust gas containing nitrogen oxides are brought into contact with each other, C 2 H 4 , C 3 H 6 , and C 3 H 8 as reducing agents are introduced into the exhaust gas atmosphere.
Hydrocarbons etc., CH 3 OH, and alcohols such as C 2 H 5 OH, contain a carbon gas or the like having a reducing CO or the like, when contacted with the catalyst material, NO X reducing is further increased .

【0023】[0023]

【作用】本発明の窒素酸化物除去用酸化物触媒材料並び
に窒素酸化物除去方法によれば、酸化物触媒材料は、N
i及びGaを主たる金属元素として含有し、結晶相がス
ピネル型構造を有する複合酸化物と、Al2 3 を混合
した担持体に、白金(Pt)またはパラジウム(Pd)
を前記担持体100重量部に対して0.01〜1.0重
量部担持したことから、前記担持体上においてNOの酸
化反応により生成したNO2 と担持した前記貴金属によ
り活性化された炭化水素が反応し、350℃以下の低温
度域においてもNO還元活性を示す。
According to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material is N
Platinum (Pt) or palladium (Pd) was added to a carrier in which a complex oxide containing i and Ga as main metal elements and having a crystal phase having a spinel structure and Al 2 O 3 was mixed.
Since 0.01 to 1.0 part by weight was carried with respect to 100 parts by weight of the carrier, the hydrocarbon activated by the NO 2 carried by the NO 2 produced by the oxidation reaction of NO on the carrier and the noble metal carried by the carrier. Reacts and exhibits NO reduction activity even in a low temperature range of 350 ° C. or lower.

【0024】[0024]

【実施例】以下、本発明の窒素酸化物除去用酸化物触媒
材料並びに窒素酸化物除去方法について、実施例に基づ
き詳細に述べる。
EXAMPLES Hereinafter, the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention will be described in detail based on examples.

【0025】本発明の窒素酸化物除去用酸化物触媒材料
は、Ni及びGaを含有する原料粉末を所定量秤量し、
十分に攪拌混合した後、Al2 3 粉末を添加し、酸化
雰囲気中、500〜1600℃の温度で5〜30時間熱
処理することにより、Ni及びGaを主たる金属元素と
するスピネル型結晶の複合酸化物とAl2 3 から成る
混合粉末が得られる。
The oxide catalyst material for removing nitrogen oxides of the present invention is obtained by weighing a predetermined amount of raw material powder containing Ni and Ga,
After sufficiently stirring and mixing, Al 2 O 3 powder was added, and heat treatment was performed at a temperature of 500 to 1600 ° C. for 5 to 30 hours in an oxidizing atmosphere to form a composite of spinel-type crystals containing Ni and Ga as main metal elements. A mixed powder of oxide and Al 2 O 3 is obtained.

【0026】次いで、前記混合粉末を担持体として、所
定量の貴金属を含有する水溶液を加えて蒸発乾固し、ヘ
リウム(He)気体中、400〜600℃の温度で3〜
5時間熱処理して本発明の酸化物触媒材料が得られる。
Next, using the mixed powder as a carrier, an aqueous solution containing a predetermined amount of a noble metal is added, and the mixture is evaporated to dryness, and then heated in a helium (He) gas at a temperature of 400 to 600 ° C. for 3 to 3.
After heat treatment for 5 hours, the oxide catalyst material of the present invention is obtained.

【0027】前記原料粉末としては、例えば、Ni及び
Gaの酸化物や、熱処理により酸化物を生成するそれら
の炭酸塩、硝酸塩、酢酸塩等を用いることができる。
As the raw material powder, for example, oxides of Ni and Ga, and their carbonates, nitrates, acetates and the like which generate oxides by heat treatment can be used.

【0028】また、前記原料粉末は、定比のスピネル型
構造を示すNiGa2 4 にGa金属を固溶することに
よりNOX の還元分解特性が向上すると考えられること
から、Niに対するGaの金属元素比が2.1以上にな
るように配合することが望ましい。
Further, it is considered that the raw material powder improves the reductive decomposition property of NO x by solid-dissolving Ga metal in NiGa 2 O 4 having a stoichiometric spinel structure. It is desirable to mix them so that the element ratio is 2.1 or more.

【0029】更に、前記複合酸化物は、前記以外に酸化
物や他の金属塩による固相反応や、金属アルコキシド等
のゾル−ゲル法等により合成できるものであり、何等こ
れらの製造方法に限定されるものではない。
Further, the above-mentioned composite oxide can be synthesized by a solid-phase reaction with oxides or other metal salts other than the above, or by a sol-gel method of metal alkoxide, etc., and is not limited to these production methods. It is not something that will be done.

【0030】前記混合粉末の熱処理は、その温度が50
0℃より低いと結晶化が不充分となり、逆に1600℃
を越えると緻密化してしまうため、500〜1600℃
の温度で、酸化雰囲気中、5〜30時間行うが、特に低
い温度で熱処理することが粉末の比表面積を高めるため
に有効であり、実用的には、比表面積が60m2 /g以
上となるように設定することが望ましい。
The temperature of the heat treatment of the mixed powder is 50
If the temperature is lower than 0 ℃, the crystallization will be insufficient, and conversely 1600 ℃.
If it exceeds, it will be densified, so it is 500-1600 ℃
At a temperature of 5 to 30 hours in an oxidizing atmosphere, but heat treatment at a particularly low temperature is effective for increasing the specific surface area of the powder, and practically the specific surface area is 60 m 2 / g or more. It is desirable to set

【0031】次に、本発明を評価するに際し、出発原料
としてNi(NO3 2 ・6H2 OとGa(NO3 3
・9H2 Oの試薬を用い、NiとGaの金属元素比が
1:3となるように秤量し、これら試薬を蒸留水中に溶
解させ、撹拌しながらアンモニア水で中和し、この時、
生成した沈澱物の泥漿100重量部にAl2 3 の粉末
を、50重量部添加し、超音波乳化分散機で十分に攪拌
混合した後、これを凍結乾燥させた。
Next, in evaluating the present invention, Ni (NO 3 ) 2 .6H 2 O and Ga (NO 3 ) 3 were used as starting materials.
-Using a reagent of 9H 2 O, weighed so that the metal element ratio of Ni and Ga was 1: 3, dissolved these reagents in distilled water, and neutralized with ammonia water while stirring.
50 parts by weight of Al 2 O 3 powder was added to 100 parts by weight of the resulting precipitate, and the mixture was sufficiently stirred and mixed by an ultrasonic emulsification disperser, and then freeze-dried.

【0032】次に、該乾燥粉末を大気中、700℃の温
度で30時間、熱処理した後、該粉末に、表1に示す量
の各貴金属を含有する水溶液を添加し、蒸発乾固した
後、ヘリウム(He)気流中、500℃の温度で3時間
熱処理した。
Next, the dry powder was heat-treated in the air at a temperature of 700 ° C. for 30 hours, then an aqueous solution containing each noble metal in an amount shown in Table 1 was added to the powder, and the mixture was evaporated to dryness. In a helium (He) stream, heat treatment was performed at a temperature of 500 ° C. for 3 hours.

【0033】その後、前記貴金属を担持した粉末を金型
プレスにより成形後、CIP成形し、該成形体を解砕し
て篩別し、500μmを越え、700μm以下に整粒し
て評価用試料を調製した。
Thereafter, the powder carrying the noble metal is molded by a die press, CIP-molded, the molded body is crushed and sieved, and the size of the powder exceeds 500 μm and 700 μm or less to obtain a sample for evaluation. Prepared.

【0034】尚、前記担持体に貴金属を全く担持しない
ものを比較例とした。
A comparative example was one in which no noble metal was supported on the carrier.

【0035】かくして得られた評価用試料の蛍光X線分
析により求めたNiに対するGaのカウント比は、1.
93であった。
The count ratio of Ga to Ni obtained by fluorescent X-ray analysis of the evaluation sample thus obtained was 1.
It was 93.

【0036】また、X線回折測定(XRD)により結晶
相を同定し、結晶相がスピネル結晶とγ−Al2 3
から成ることを確認した。
Further, the crystal phase was identified by X-ray diffraction measurement (XRD), and it was confirmed that the crystal phase consisted of a spinel crystal and a γ-Al 2 O 3 phase.

【0037】次いで、NOが1000ppm、O2 が1
0%、H2 Oが10%、還元剤としてC2 4 が100
0ppm、残部がHeから成る水蒸気を含有した反応ガ
スを、該反応ガスと触媒材料が接触する条件として、W
/Fを0.03g・sec/ccに設定し、前記評価用
試料を充填した触媒層に流し、200〜600℃の温度
範囲でNOの還元により生成したN2 をガスクロマトグ
ラフで測定し、N2 の生成量から各温度でのNO転換率
を求めた。
Next, NO of 1000 ppm and O 2 of 1
0%, H 2 O 10%, C 2 H 4 100 as reducing agent
A reaction gas containing water vapor of 0 ppm and the rest being He is used as a condition for contacting the reaction gas with the catalyst material.
/ F was set to 0.03 g · sec / cc, the sample for evaluation was flowed through the catalyst layer, and N 2 produced by the reduction of NO was measured in a temperature range of 200 to 600 ° C. by a gas chromatograph. The NO conversion rate at each temperature was determined from the amount of 2 produced.

【0038】その結果、前記測定温度範囲内で白金(P
t)を担持した酸化物触媒材料は、350℃以下の低温
域で広範囲にNO還元活性を示すものを良と評価した。
As a result, the platinum (P
The oxide catalyst material supporting t) was evaluated as good when it exhibits NO reduction activity in a wide range in a low temperature range of 350 ° C. or lower.

【0039】また、パラジウム(Pd)を担持した酸化
物触媒材料は、350℃から500℃の温度範囲でNO
還元活性を示すものを良と評価した。
The oxide catalyst material supporting palladium (Pd) is NO in the temperature range of 350 ° C to 500 ° C.
Those showing reduction activity were evaluated as good.

【0040】[0040]

【表1】 [Table 1]

【0041】表1から明らかなように、比較例である貴
金属を担持しない試料番号1は、350℃以下の温度で
はNO還元活性を全く示さず、また本発明の請求範囲外
である資料番号9、17は、いずれも所定温度域でのN
O還元活性が全体に低く、実用的でない。
As is clear from Table 1, the sample No. 1, which is a comparative example and does not carry a noble metal, shows no NO reducing activity at a temperature of 350 ° C. or lower, and the document No. 9 is out of the scope of the present invention. , 17 are N in the predetermined temperature range
O-reduction activity is low overall and not practical.

【0042】それに対して、本発明では白金(Pt)担
持酸化物触媒は350℃以下の低温度域で高いNO還元
活性を示し、またパラジウム(Pd)担持酸化物触媒は
350℃以下は勿論、500℃までの広い温度範囲で十
分なNO還元活性を示していることが分かる。
On the other hand, in the present invention, the platinum (Pt) -supported oxide catalyst exhibits a high NO reduction activity in the low temperature range of 350 ° C. or lower, and the palladium (Pd) -supported oxide catalyst does not exceed 350 ° C. It can be seen that sufficient NO reduction activity is exhibited in a wide temperature range up to 500 ° C.

【0043】また、前記評価用試料を用い、4気筒のデ
ィーゼルエンジン台上試験装置の排気管に取り付け、該
ディーゼルエンジンを最高回転数、全負荷の条件で10
0時間運転する耐久試験を実施し、試験後の評価用試料
について前記同様にしてNO還元活性を評価したが、N
O転換率はほとんど低下していないことが確認でき、耐
水性、耐熱性に優れていることも証明された。
Further, using the above-mentioned sample for evaluation, it was attached to the exhaust pipe of a four-cylinder diesel engine bench test apparatus, and the diesel engine was operated under the conditions of maximum rotation speed and full load.
A durability test of running for 0 hours was carried out, and the NO reduction activity of the evaluation sample after the test was evaluated in the same manner as described above.
It was confirmed that the O conversion rate did not almost decrease, and it was also proved that the water resistance and heat resistance were excellent.

【0044】[0044]

【発明の効果】以上、詳述したように本発明の窒素酸化
物除去用酸化物触媒材料並びに窒素酸化物除去方法によ
れば、該酸化物触媒材料はNiとGaを主たる金属元素
として含有するスピネル型構造の複合酸化物にAl2
3 を混合した担持体に、白金(Pt)またはパラジウム
(Pd)を前記担持体100重量部に対して0.01〜
1.0重量部担持したものであり、高濃度の酸素と還元
性を有する炭素含有ガスが存在する酸化雰囲気中で、前
記酸化物触媒材料と窒素酸化物を含む排気ガスを接触さ
せることから、水蒸気が存在する雰囲気中は勿論、排気
ガス中の酸素濃度が3%以上の高酸素濃度雰囲気下であ
っても、その上、ガスの流速が高速度であっても、優れ
たNOX 還元性能を有し、排気ガス中に含まれるNOX
を有効に還元除去することができる。
As described above in detail, according to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material contains Ni and Ga as main metal elements. Al 2 O for spinel type complex oxide
Platinum (Pt) or palladium (Pd) is added to the carrier mixed with 3 in an amount of 0.01 to 100 parts by weight of the carrier.
1.0 parts by weight is supported, and since the oxide catalyst material and the exhaust gas containing nitrogen oxide are contacted in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present, Excellent NO X reduction performance not only in an atmosphere in which water vapor exists but also in an atmosphere with a high oxygen concentration of 3% or more in the exhaust gas, as well as at a high gas flow rate. NO x contained in exhaust gas
Can be effectively reduced and removed.

【0045】その結果、省エネルギー、省資源及び地球
温暖化防止を目標として開発される今後のディーゼルエ
ンジンやリーンバーンエンジン等の各種内燃機関の排気
ガスをはじめ、NOX を含有する各種有害物質の浄化に
極めて有用なものとなる。
As a result, purification of various harmful substances containing NO x , including exhaust gas from various internal combustion engines such as diesel engines and lean burn engines, which are developed for the purpose of energy saving, resource saving and prevention of global warming. It will be extremely useful for

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】ニッケル(Ni)とガリウム(Ga)を主
たる金属元素として含有するスピネル型構造の複合酸化
物とアルミナ(Al2 3 )とを混合した担持体に、白
金(Pt)またはパラジウム(Pd)を前記担持体10
0重量部に対して0.01〜1.0重量部担持したこと
を特徴とする窒素酸化物除去用酸化物触媒材料。
1. Platinum (Pt) or palladium is added to a carrier in which a composite oxide having a spinel structure containing nickel (Ni) and gallium (Ga) as main metal elements is mixed with alumina (Al 2 O 3 ). (Pd) as the carrier 10
An oxide catalyst material for removing nitrogen oxides, which is carried in an amount of 0.01 to 1.0 parts by weight based on 0 parts by weight.
【請求項2】前記白金(Pt)を前記担持体100重量
部に対して0.03〜1.0重量部、または前記パラジ
ウム(Pd)を前記担持体100重量部に対して0.0
1〜0.7重量部担持したことを特徴とする請求項1記
載の窒素酸化物除去用酸化物触媒材料。
2. The platinum (Pt) is 0.03 to 1.0 part by weight with respect to 100 parts by weight of the carrier, or the palladium (Pd) is 0.0 with respect to 100 parts by weight of the carrier.
The oxide catalyst material for removing nitrogen oxides according to claim 1, which is carried in an amount of 1 to 0.7 parts by weight.
【請求項3】前記白金(Pt)を前記担持体100重量
部に対して0.03〜0.7重量部、または前記パラジ
ウム(Pd)を前記担持体100重量部に対して0.0
1〜0.5重量部担持したことを特徴とする請求項1及
び請求項2記載の窒素酸化物除去用酸化物触媒材料。
3. The platinum (Pt) is 0.03 to 0.7 parts by weight with respect to 100 parts by weight of the carrier, or the palladium (Pd) is 0.0 with respect to 100 parts by weight of the carrier.
The oxide catalyst material for removing nitrogen oxides according to claim 1 or 2, wherein 1 to 0.5 part by weight is supported.
【請求項4】高濃度の酸素と還元性を有する炭素含有ガ
スが存在する酸化雰囲気中で、ニッケル(Ni)とガリ
ウム(Ga)を主たる金属元素として含有するスピネル
型構造の複合酸化物とアルミナ(Al2 3 )を混合し
た担持体に、白金(Pt)またはパラジウム(Pd)を
前記担持体100重量部に対して0.01〜1.0重量
部担持して成る酸化物触媒材料を、窒素酸化物を含む排
気ガスに接触させることを特徴とする窒素酸化物除去方
法。
4. A composite oxide having a spinel structure and nickel containing nickel (Ni) and gallium (Ga) as main metal elements in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. An oxide catalyst material obtained by supporting platinum (Pt) or palladium (Pd) on a support mixed with (Al 2 O 3 ) in an amount of 0.01 to 1.0 part by weight based on 100 parts by weight of the support. A method for removing nitrogen oxide, comprising contacting with exhaust gas containing nitrogen oxide.
【請求項5】前記白金(Pt)を前記担持体100重量
部に対して0.03〜1.0重量部、または前記パラジ
ウム(Pd)を前記担持体100重量部に対し0.01
〜0.7重量部担持して成る酸化物触媒材料を、窒素酸
化物を含む排気ガスに接触させることを特徴とする請求
項4記載の窒素酸化物除去方法。
5. The platinum (Pt) is 0.03 to 1.0 part by weight with respect to 100 parts by weight of the carrier, or the palladium (Pd) is 0.01 with respect to 100 parts by weight of the carrier.
5. The method for removing nitrogen oxides according to claim 4, wherein the oxide catalyst material supported by about 0.7 parts by weight is brought into contact with exhaust gas containing nitrogen oxides.
【請求項6】前記白金(Pt)を前記担持体100重量
部に対し0.03〜0.7重量部、または前記パラジウ
ム(Pd)を前記担持体100重量部に対し0.01〜
0.5重量部担持して成る酸化物触媒材料を、窒素酸化
物を含む排気ガスに接触させることを特徴とする請求項
4及び請求項5記載の窒素酸化物除去方法。
6. The platinum (Pt) is 0.03 to 0.7 part by weight with respect to 100 parts by weight of the carrier, or the palladium (Pd) is 0.01 to 0.7 part by weight with respect to 100 parts by weight of the carrier.
The method for removing nitrogen oxides according to claim 4 or 5, wherein the oxide catalyst material supported by 0.5 parts by weight is brought into contact with exhaust gas containing nitrogen oxides.
JP7063809A 1995-03-23 1995-03-23 Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide Pending JPH08257404A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7063809A JPH08257404A (en) 1995-03-23 1995-03-23 Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7063809A JPH08257404A (en) 1995-03-23 1995-03-23 Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide

Publications (1)

Publication Number Publication Date
JPH08257404A true JPH08257404A (en) 1996-10-08

Family

ID=13240082

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7063809A Pending JPH08257404A (en) 1995-03-23 1995-03-23 Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide

Country Status (1)

Country Link
JP (1) JPH08257404A (en)

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